materials
Article
Carbon Adsorbents from Spent Coffee for Removal of
Methylene Blue and Methyl Orange from Water
Inga Block
1
, Christina Günter
2
, Alysson Duarte Rodrigues
3
, Silvia Paasch
4
, Peter Hesemann
3
and Andreas Taubert
1,
*
Citation: Block, I.; Günter, C.; Duarte
Rodrigues, A.; Paasch, S.; Hesemann,
P.; Taubert, A. Carbon Adsorbents
from Spent Coffee for Removal of
Methylene Blue and Methyl Orange
from Water. Materials 2021, 14, 3996.
https://doi.org/10.3390/ma14143996
Academic Editor: Zhenghong Huang
Received: 20 May 2021
Accepted: 1 July 2021
Published: 16 July 2021
Publisher’s Note: MDPI stays neutral
with regard to jurisdictional claims in
published maps and institutional affil-
iations.
Copyright: © 2021 by the authors.
Licensee MDPI, Basel, Switzerland.
This article is an open access article
distributed under the terms and
conditions of the Creative Commons
Attribution (CC BY) license (https://
creativecommons.org/licenses/by/
4.0/).
1
Institut für Chemie, Universität Potsdam, Karl-Liebknecht-Straße 24-25, D-14476 Potsdam, Germany;
iblock@uni-potsdam.de
2
Institut für Geowissenschaften, Universität Potsdam, Karl-Liebknecht-Straße 24-25, D-14476 Potsdam, Germany;
guenter@geo.uni-potsdam.de
3
ICGM, Univ Montpellier-CNRS-ENSCM, 34090 Montpellier, France;
alysson.duarte-rodrigues@umontpellier.fr (A.D.R.); peter.hesemann@umontpellier.fr (P.H.)
4
Professur für Bioanalytische Chemie, TU Dresden, Bergstraße 66, D-01062 Dresden, Germany;
silvia.paasch@tu-dresden.de
* Correspondence: ataubert@uni-potsdam.de; Tel.: +49-(0)3-3197-75773
Abstract: Activated carbons (ACs) were prepared from dried spent coffee (SCD), a biological waste
product, to produce adsorbents for methylene blue (MB) and methyl orange (MO) from aqueous
solution. Pre-pyrolysis activation of SCD was achieved via treatment of the SCD with aqueous
sodium hydroxide solutions at 90
◦
C. Pyrolysis of the pretreated SCD at 500
◦
C for 1 h produced
powders with typical characteristics of AC suitable and effective for dye adsorption. As an alternative
to the rather harsh base treatment, calcium carbonate powder, a very common and abundant resource,
was also studied as an activator. Mixtures of SCD and CaCO
3
(1:1 w/w) yielded effective ACs for
MO and MB removal upon pyrolysis needing only small amounts of AC to clear the solutions.
A selectivity of the adsorption process toward anionic (MO) or cationic (MB) dyes was not observed.
Keywords: water; spent coffee; dye adsorption; methylene blue; methyl orange; calcium carbonate;
activated carbon; water treatment; dye removal
1. Introduction
Water is among the most valuable resources worldwide. As a result, reliable methods
for water treatment and remediation are among the most pressing issues worldwide. In
addition to natural organic matter, heavy metals, biological contaminants, and disinfection
byproducts are among the key pollutants in surface and drinking water. Synthetic organic
substances such as dyes, oils, or pharmaceuticals and their metabolites or degradation
products also play a major role in water pollution [1].
Many of these substances can be removed from the aqueous phase by activated
carbon (AC) adsorbents. AC can be produced on an industrial scale from sources such
as coal, petroleum, or coconut husk [2,3]. As a general requirement, the starting material
needs to have a high carbon content, and many renewable raw materials are therefore
candidates for AC production. Typical ACs have large surface areas between 500 and
1500 m
2
/g and pore volumes of up to 1.8 cm
3
/g [1]. Therefore, many groups have studied
a diverse pool of natural (waste) products such as coconut shells, fruit seeds (grapes,
pomegranate, date palm), olive and peach stones, wood wastes, pine cones, and more for
the fabrication of ACs [4–20]. Other studies include composites of clay and carbonaceous
materials [6,21–23]. For example, Okman and Karagöz et al. [10] chemically activated
grape seeds with potassium carbonate and potassium hydroxide before carbonization
between 600 and 800
◦
C, resulting in materials with BET surface areas of up to 1238 m
2
/g
(K
2
CO
3
) and 1222 m
2
/g (KOH).
Materials 2021, 14, 3996. https://doi.org/10.3390/ma14143996 https://www.mdpi.com/journal/materials